GMSMON-17 WILLISTON RESERVOIR TRIBUTARY - BC Hydro
GMSMON-17 WILLISTON RESERVOIR TRIBUTARY - BC Hydro
GMSMON-17 WILLISTON RESERVOIR TRIBUTARY - BC Hydro
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
May 22, 2012<br />
Report No. 1114920016-R-Rev0-2000 8<br />
<strong>GMSMON</strong>-<strong>17</strong> <strong>WILLISTON</strong> <strong>RESERVOIR</strong> <strong>TRIBUTARY</strong> HABITAT<br />
REVIEW<br />
two people netting fish. Sampling crews were consistent for all removal passes at each site to keep capture<br />
efficiency consistent between passes. Each site was sampled from downstream to upstream. Captured fish were<br />
transferred to buckets set along the side of the sample reach. Fish observed but not captured were recorded,<br />
including the species and estimated length when possible. Sampling effort (i.e., seconds of electrofisher<br />
operation) was recorded during each removal pass. All captured fish were enumerated, identified to species,<br />
measured for fork length (to the nearest 1 mm) and weighed (to the nearest 1 g). Scale samples were collected<br />
from salmonid species and stored in scale envelopes. After processing fish from the first electrofishing pass, a<br />
second pass was conducted in the same manner. Because of low catch rates of fish in the study sites, only<br />
two electrofishing passes were conducted at most sites, with only one pass at sites with no fish or very few fish<br />
captured (see Results Section 3.0). After all electrofishing passes were completed, fish were released back into<br />
the creek within the sample site.<br />
Table 4 provides detailed information on the sample sites, site conditions, sampling effort, and electrofisher<br />
settings used during the sampling. Maps 2 to 5 in Appendix A show the location of the block nets in each of the<br />
sampled tributaries.